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      Isotopic Exchange between Aqueous Fe(II) and Solid Fe(III) in Lake Sediment—A Kinetic Assemblage Approach

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          Abstract

          The catalytic effect of aqueous Fe(II) (Fe 2+ aq) on the transformation of Fe(oxyhydr)oxides has been extensively studied in the laboratory. It involves the transfer of electrons between Fe 2+ aq and Fe-(oxyhydr)oxides, rapid atomic exchange of Fe between the two states, and recrystallization of the Fe-oxides into more stable Fe-(oxyhydr)oxides. The potential occurrence of these reactions in natural soils and sediments can have an important impact on biogeochemical cycling of iron, carbon, and phosphorus. We investigated the possible isotopic exchange between Fe 2+ aq and sedimentary Fe(III) in Fe–Si–C-rich lake sediments. 57Fe Mössbauer spectroscopy was used to evaluate Fe mineral speciation in unaltered lake sediments. Unaltered and oxidized sediment laboratory incubations were coupled with a classical kinetic approach that allows a quantitative description of the reactivity of assemblages of Fe-(oxyhydr)oxides found in sediments. Specifically, unaltered and oxidized sediment samples were separately incubated with an 55Fe 2+ aq-enriched solution and exchange was observed between 55Fe 2+ aq and sedimentary Fe(III), highest in the top of the sediment and decreasing with depth with the 55Fe 2+ aq tracer distributed within the bulk of the sedimentary Fe(III) phase. Our results indicate that atomic exchange between Fe 2+ aq and sedimentary Fe(III) occurs in natural sediments with electrons transferred from the Fe(III)-particle to Fe(III)-particle via Fe 2+ aq intermediates.

          Abstract

          This study illustrates atomic exchange between Fe 2+ aq and sedimentary Fe(III) in natural sediments potentially controlling the mobility of P and other contaminants binding to Fe-(oxyhydr)oxides.

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          Filamentous bacteria transport electrons over centimetre distances.

          Oxygen consumption in marine sediments is often coupled to the oxidation of sulphide generated by degradation of organic matter in deeper, oxygen-free layers. Geochemical observations have shown that this coupling can be mediated by electric currents carried by unidentified electron transporters across centimetre-wide zones. Here we present evidence that the native conductors are long, filamentous bacteria. They abounded in sediment zones with electric currents and along their length they contained strings with distinct properties in accordance with a function as electron transporters. Living, electrical cables add a new dimension to the understanding of interactions in nature and may find use in technology development.
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            The interplay of microbially mediated and abiotic reactions in the biogeochemical Fe cycle.

            Many iron (Fe) redox processes that were previously assumed to be purely abiotic, such as photochemical Fe reactions, are now known to also be microbially mediated. Owing to this overlap, discerning whether biotic or abiotic processes control Fe redox chemistry is a major challenge for geomicrobiologists and biogeochemists alike. Therefore, to understand the network of reactions within the biogeochemical Fe cycle, it is necessary to determine which abiotic or microbially mediated reactions are dominant under various environmental conditions. In this Review, we discuss the major microbially mediated and abiotic reactions in the biogeochemical Fe cycle and provide an integrated overview of biotic and chemically mediated redox transformations.
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              The anaerobic degradation of organic matter in Danish coastal sediments: iron reduction, manganese reduction, and sulfate reduction.

              We used a combination of porewater and solid phase analysis, as well as a series of sediment incubations, to quantify organic carbon oxidation by dissimilatory Fe reduction, Mn reduction, and sulfate reduction, in sediments from the Skagerrak (located off the northeast coast of Jutland, Denmark). In the deep portion of the basin, surface Mn enrichments reached 3.5 wt%, and Mn reduction was the only important anaerobic carbon oxidation process in the upper 10 cm of the sediment. In the less Mn-rich sediments from intermediate depths in the basin, Fe reduction ranged from somewhat less, to far more important than sulfate reduction. Most of the Mn reduction in these sediments may have been coupled to the oxidation of acid volatile sulfides (AVS), rather than to dissimilatory reduction. High rates of metal oxide reduction at all sites were driven by active recycling of both Fe and Mn, encouraged by bioturbation. Recycling was so rapid that the residence time of Fe and Mn oxides, with respect to reduction, ranged from 70-250 days. These results require that, on average, an atom of Fe or Mn is oxidized and reduced between 100-300 times before ultimate burial into the sediment. We observed that dissolved Mn2+ was completely removed onto fully oxidized Mn oxides until the oxidation level of the oxides was reduced to about 3.8, presumably reflecting the saturation by Mn2+ of highly reactive surface adsorption sites. Fully oxidized Mn oxides in sediments, then, may act as a cap preventing Mn2+ escape. We speculate that in shallow sediments of the Skagerrak, surface Mn oxides are present in a somewhat reduced oxidation level (< 3.8) allowing Mn2+ to escape, and perhaps providing the Mn2+ which enriches sediments of the deep basin.
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                Author and article information

                Journal
                Environ Sci Technol
                Environ Sci Technol
                es
                esthag
                Environmental Science & Technology
                American Chemical Society
                0013-936X
                1520-5851
                11 March 2025
                25 March 2025
                : 59
                : 11
                : 5534-5544
                Affiliations
                []Department of Civil, Structural and Environmental Engineering, Trinity College Dublin , College Green, Museum Building, D02 PN40 Dublin 2, Ireland
                []Department of Plant and Environmental Sciences, University of Copenhagen , DK-1871 Copenhagen, Denmark
                [§ ]Bayerisches Geoinstitut, University of Bayreuth , 95440 Bayreuth, Germany
                []School of Earth Sciences, University of Bristol , BS8 1RJ Bristol, U.K.
                []Department of Chemical and Biochemical Engineering Bio Conversions, Technical University of Denmark , DK-2800 Lyngby, Denmark
                [# ]Nordic Center for Earth Evolution, Institute of Biology, University of Southern Denmark , DK 5230 Odense M, Denmark
                []GEUS, Geological Survey of Denmark and Greenland , DK-1350 Copenhagen, Denmark
                Author notes
                Author information
                https://orcid.org/0000-0002-1974-8145
                https://orcid.org/0000-0002-4399-7336
                https://orcid.org/0000-0002-9711-763X
                https://orcid.org/0000-0002-1221-7077
                https://orcid.org/0000-0002-8617-2393
                https://orcid.org/0000-0002-4060-8382
                Article
                10.1021/acs.est.4c07369
                11948465
                40067284
                be097e2e-4c88-477a-9cd7-74f304d33a8c
                © 2025 The Authors. Published by American Chemical Society

                Permits the broadest form of re-use including for commercial purposes, provided that author attribution and integrity are maintained ( https://creativecommons.org/licenses/by/4.0/).

                History
                : 19 July 2024
                : 04 March 2025
                : 03 March 2025
                Funding
                Funded by: Natur og Univers, Det Frie Forskningsråd, doi 10.13039/100008394;
                Award ID: 09-064296
                Funded by: UK Research and Innovation, doi 10.13039/100014013;
                Award ID: MR/V023918/1
                Categories
                Article
                Custom metadata
                es4c07369
                es4c07369

                General environmental science
                isotope exchange,fe-(oxyhydr)oxides,radioisotopes,kinetic assemblage,fe2+aq,contaminant mobilization,aquatic ecosystems

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